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microorganisms

Article Temporal Dynamics of Bacterial Communities in a Pilot-Scale Vermireactor Fed with Distilled Grape Marc

1, , 1, 2 3,4 María Gómez-Brandón * †, Manuel Aira †, Natielo Santana , Marcos Pérez-Losada and Jorge Domínguez 1

1 Grupo de Ecoloxía (GEA), Universidade de Vigo, E-36310 Vigo, Spain; [email protected] (M.A.); [email protected] (J.D.) 2 Department of Science, Federal University of Santa Maria, 97119-900 Santa Maria, Rio Grande do Sul, Brazil; [email protected] 3 Computational Biology Institute, Department of Biostatistics and Bioinformatics, Milken Institute School of Public Health, George Washington University, Washington, DC 20052, USA; [email protected] 4 CIBIO-InBIO, Centro de Investigação em Biodiversidade e Recursos Genéticos, Universidade do Porto, Campus Agrário de Vairão, 4485-661 Vairão, Portugal * Correspondence: [email protected] These authors contributed equally to this work. †  Received: 18 March 2020; Accepted: 25 April 2020; Published: 28 April 2020 

Abstract: Vermicomposting has been found as a profitable approach to dispose of and treat large quantities of raw grape marc. However, less information is available with regard to its efficiency for treating distillery winery byproducts, even though distillation has been widely used as a way to economically valorize grape marc. As such, we sought to characterize the compositional and functional changes in bacterial communities during vermicomposting of distilled grape marc by using 16S rRNA high-throughput sequencing. Samples were collected at the initiation of vermicomposting and at days 14, 21, 28, 35 and 42. There were significant changes (p < 0.0001) in the bacterial community composition of distilled grape marc after 14 days of vermicomposting that were accompanied by twofold increases in bacterial richness and diversity from a taxonomic and phylogenetic perspective. This was followed by significant increases in functional diversity of the bacterial community, including metabolic capacity, lignin and cellulose metabolism, and salicylic acid synthesis. These findings indicate that the most striking compositional and functional bacterial community changes took place during the active phase of the process. They also pinpoint functional attributes that may be related to the potential beneficial effects of distilled grape marc vermicompost when applied on soil and .

Keywords: winery byproducts; steam distillation; earthworms; microbial communities; vermicompost; 16S rRNA; metagenomics

1. Introduction Grape marc, the major solid byproduct of the winemaking industry, has been used as an additive in animal feeding [1], and as a soil conditioner owing to its high level of and macronutrients [2–7]. This winery byproduct is also sent to distilleries, to recover ethanol for its further use in the elaboration of alcoholic beverages [8,9], and to cosmetic and pharmaceutical industries [6]. Moreover, grape marc can represent a valuable alternative to replace fossil fuels by means of bioethanol generation through distillation [10]. Altogether, it makes distillation a profitable way to economically valorize grape marc.

Microorganisms 2020, 8, 642; doi:10.3390/microorganisms8050642 www.mdpi.com/journal/microorganisms Microorganisms 2020, 8, 642 2 of 19

Nevertheless, the process of distillation also involves the generation of liquid and solid distillery effluents such as vinasses and distilled grape marc that must be treated, disposed of or reused properly to avoid negative environmental impacts [11]. As in raw grape marc, the low pH and the presence of phytotoxic and antimicrobial compounds make distilled grape marc a troublesome waste stream product, which, if not properly treated, can cause soil acidification, groundwater pollution and oxygen depletion in soil [12]. In this sense, stabilization of distilled grape marc via composting has been explored [12–15]. However, the low pH of distilled grape marc poses challenges for large-scale composting trials because it could inhibit the transition between mesophilic and thermophilic composting phases [13]. Co-composting of distilled grape marc with other organic materials like green waste has been shown as a more effective alternative improving not only the quality but also shortening the time required to achieve stabilization [14]. Vermicomposting has also been successfully used to dispose of and treat large quantities of raw grape marc [2–7,16,17]. On the one hand, it may provide a means to neutralize the pH of this winery byproduct, as previously shown by Domínguez et al. [2]. And, on the other hand, vermicomposting has been shown to effectively reduce organic biomass and generate high-quality fertilizer with beneficial effects on soil and plants [18,19]. Nonetheless, there is scarce information about the feasibility of vermicomposting for treating distillery residues [20]. Both raw and distilled grape marc are expected to differ in their autochthonous microbiota likely due to the strong selective pressures exerted by high ethanol concentrations, low pH, low oxygen levels and temperature fluctuations in the microbial composition of raw grape marc throughout the distillation process [21]. Such differences in the initial microbial composition of the starting materials may have important consequences for driving bacterial succession during the vermicomposting process [22]. The temporal shifts in microbial communities during vermicomposting can be seen as an example of heterotrophic ecological succession driven by changes in both the quantity and quality of available organic carbon sources. The early changes in the community composition are mainly represented by that have recently passed through the earthworm gut and been excreted [23]. These egested materials act as a source of microorganisms and nutrients, and their rapid will result in the release of labile nutrient pools supporting the growth of copiotrophic bacteria, which are characterized by faster rates of carbon turnover, at the earlier time points. As microbial succession progresses, copiotrophic groups will be replaced by oligotrophic bacteria with a higher substrate utilization efficiency and the ability to metabolize the remaining recalcitrant substrates in the casts during the maturation stage [24]. By using sequencing-based analyses it has enabled us to enhance the throughput, and phylogenetically group and name a larger number of bacterial taxa in the vermicompost microbiome, as recently described for raw grape marc-derived vermicomposts of the cultivars Albariño [25] and Mencía [7]. Moreover, the application of high-throughput sequencing approaches has also facilitated the identification of bacterial taxa that drive keystone functions that may explain the beneficial effects of vermicomposts when applied to the soil and plants [25,26]. However, it is not known yet if the bacterial communities involved in the various stages of vermicomposting of marcs derived from the distillation process will undergo similar compositional and functional changes as those reported for raw grape marc over the course of the process. Therefore, the aim of the present study was to characterize the taxonomic and functional diversity of the bacterial communities involved in the vermicomposting of distilled grape marc of Vitis vinifera L. cv. Albariño in a pilot-scale vermireactor by means of 16S rRNA high-throughput sequencing.

2. Materials and Methods

2.1. Distilled Grape Marc We chose marc derived from distillation of Vitis vinifera cv. Albariño grapes since this grape variety represents 95% of the annual white grape harvest in northwestern Spain. The distilled grape marc was Microorganisms 2020, 8, 642 3 of 19

kindly supplied by a winery located in Pontevedra (Galicia, NW Spain). It was stored at 4 ◦C until needed and turned and moistened with water during two days prior to the vermicomposting trial.

2.2. Vermicomposting Set-Up and Sampling Design The distilled grape marc was processed in a rectangular metal pilot-scale vermireactor (4 m long 1.5 m wide 1 m high) housed in a greenhouse with no temperature control over × × a period of 42 days. The vermireactor set-up has been previously described by Kolbe et al. [25]. The population density of earthworms (Eisenia andrei) was close to its maximum capacity, having a value of 10,923 1783 individuals m 2 that corresponds to 289 72 mature earthworms m 2 and ± − ± − 10,634 1767 immatures m 2, with a mean biomass of 1704 251 g m 2. The earthworm population ± − ± − density in the present study was 36 times higher when compared to that in Kolbe et al. [25]. As a consequence, the vermicomposting time was shortened by half in the current study and the distilled grape marc was completely processed by the earthworms in 42 days. For the characterization of the molecular and the microbial properties, the distilled grape marc layer (12 cm height) was divided into five sections; five samples (10 g) were taken at random from each section at day 0 (fresh distilled grape marc) and after 14, 21, 28, 35 and 42 days of vermicomposting. Samples were bulked and stored in plastic bags at 80 C until needed. − ◦ 2.3. Microbial Activity

Microbial activity was assessed as basal respiration by measuring the rate of evolution of CO2 after 6 h of incubation. The evolved CO2 was trapped in NaOH and then measured by titration with HCl to a phenolphthalein endpoint after adding excess BaCl2 [27].

2.4. DNA Sequencing and Bioinformatic Analyses DNA was extracted from 0.25 g (fresh weight, fw) of distilled grape marc using the MO-BIO PowerSoil® kit (MoBio Laboratories Inc., Carlsbad, California) according to manufacturer’s protocols. DNA quality and quantity were determined using BioTek’s Take3™ Multi-Volume Plate (SinergyTM 2 Multi-Mode Microplate Reader, Bio-Tek Instruments, Inc.), as previously described by Kolbe et al. [25]. In order to describe the bacterial changes during vermicomposting of distilled grape marc, we focused on a fragment of the 16S rRNA gene covering the V4 region, by using a dual-index sequencing strategy, as described by Kozich et al. [28]. In total, 30 DNA samples representing different sampling times (0, 14, 21, 28, 35 and 42 days) were sequenced using the Illumina MiSeq platform at the Center for Michigan System, University of Michigan. The DADA2 pipeline (version 1.12) was used to infer the amplicon sequence variants (ASVs) present in each sample [29]. Standard filtering parameters were used, with forward and reverse reads truncated at 200 nt and 120 nt respectively, and with a maximum of two expected errors per read. Default settings were used for ASV inference and chimera detection. Taxonomic assignment was performed against the Silva v132 database using the assignTaxonomy function in DADA2, which implements the RDP naive Bayesian classifier [30,31]. A minimum bootstrap confidence of 80 was used for assigning . A total of 1,408,391 sequences passed all quality filters and were assigned to 3410 ASVs. Sequence data have been uploaded to the Sequence Read Archive database under accession PRJNA602410. The functional composition of the metagenomes was predicted using the Phylogenetic Investigation of Communities by Reconstruction of Unobserved States software package (PICRUSt) [32]. Predicted metagenomes were collapsed using the Kyoto Encyclopedia of Genes and Genomes (KEGG) pathway metadata [33]. Metagenome functional contributions were partitioned according to function, operational taxonomic unit (OTU), and sampled to evaluate how the OTUs responsible for specific functional roles change during vermicomposting of distilled grape marc. ASVs with less than three sequences and not present in at least 5% of the samples were removed, thus eliminating 59.88% of the ASVs but only 1.85% of the sequences. Rarefaction curves indicated that Microorganisms 2020, 8, 642 4 of 19 the sampling depth was optimal for all samples in the full data set (3410 ASVs and 1,408,391 sequences, Supplementary Figure S1) and the filtered data set (1368 ASVs and 1,382,365 sequences, Supplementary Figure S2). We normalized ASV counts using the variance-stabilizing transformation for analysis that assume homoscedasticity or could be influenced by unequal variances [34]. When analysing differential ASV abundances we normalized raw ASV counts using negative binomial models as implemented in the package DESeq2 [34,35]. Differential abundances of ASVs and other bacterial taxa ( and class) were determined according to Wald tests and p-values adjusted by false discovery rate (FDR < 0.05). Because multiple pairwise Wald tests were conducted for each pairwise time comparison (0–14, 14–21, 21–28, 28–35 and 35–42 days), we further adjusted these p-values using the Benjamini–Hochberg method to correct for multiple testing. After correction, nonsignificant contrasts were considered to have an effect size (log2-fold change) of zero. We defined the core microbiome of vermicomposting of the distilled grape marc as that comprised of ASVs present in all of the samples processed by earthworms (samples day 14 to day 42). We decided not to consider the fresh distilled grape marc because it is not an “earthworm-processed material”. An approximate maximum-likelihood phylogenetic tree was inferred using FastTree 2.1 [36]. Taxonomic α-diversity was calculated as the number of observed ASVs, and diversity and richness were estimated with the Shannon and Chao1 indexes, respectively. Phylogenetic diversity was calculated as Faith’s phylogenetic diversity [37]. Taxonomic β-diversity at the ASV level was estimated as the difference in composition of the bacterial taxonomic community between samples from different times during vermicomposting. This was done by coupling principal coordinate analysis (PCoA) with distance matrices that take the abundance of ASVs into account (Bray–Curtis) or not (Jaccard). Phylogenetic β-diversity was also estimated by PCoA of weighted (considering abundance of ASVs) and unweighted UniFrac matrix distances [38] by using the phyloseq library [34]. Mixed linear effect models were applied using the ‘nlme’ R package [39] to evaluate the effect of time on α- and β-diversity (PCoA scores) of the distilled grape marc bacterial communities. Time was the fixed factor and the effect of time nested in each sample was considered as a random factor to account for nonindependence of samples due to repeated measures. The normality of residuals and homogeneity of variance across groups was checked for each variable. The Tukey and Benjamini–Hochberg FDR tests, as implemented in the R package ‘multcomp’ [40], were used for post hoc comparisons and for multiple test corrections, respectively. Venn diagrams were constructed using the R package Vennerable [41] in order to show the number of ASVs exclusive and shared between raw and distilled grape marc samples. All analyses were performed in R version 3.5 [42], while all figures were created using the R package ggplot2 [43].

3. Results

3.1. Changes in Microbial Activity during Vermicomposting of Distilled Grape Marc Microbial activity assessed as basal respiration significantly decreased from the beginning of the experiment (day 0) until day 28, followed by no more noticeable changes until the end of the trial on day 42 (Figure1). This points to the e ffectiveness of vermicomposting at biologically stabilizing the distilled grape marc, as shown by the lower and stable values of basal respiration from day 28 onwards (Figure1). Moreover, these results indicate that the contributions of earthworms to the process can be grouped into two stages, comprising the active phase of vermicomposting (from day 0 to day 28) and the maturation (from day 28 to day 42) phase. Microorganisms 2020, 8, 642 5 of 19 Microorganisms 2020, 8, x FOR PEER REVIEW 5 of 19

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Figure 1.1. Changes in microbial activity assessed as basal respiration during vermicomposting of distilled grape marc derived from the white winemaking process of the grape variety Albariño. Individual values ( n = 5)5) are are plotted plotted for for each each time time point point an andd the the curve curve was was plotted plotted using using the the “loess” “loess” smoothing method in ggplot2 [[43].43]. 3.2. Changes in Bacterial Community Composition during Vermicomposting of Distilled Grape Marc 3.2. Changes in Bacterial Community Composition during Vermicomposting of Distilled Grape Marc accounted for the most significant proportion of bacterial communities, nearly Proteobacteria accounted for the most significant proportion of bacterial communities, nearly 50% of the sequences, in the fresh distilled grape marc (Figure2). They continued to dominate the 50% of the sequences, in the fresh distilled grape marc (Figure 2). They continued to dominate the bacterial microbiome when the initial substrate was processed by the earthworms after 14 days of bacterial microbiome when the initial substrate was processed by the earthworms after 14 days of vermicomposting (Figure2), although later on (days 21 and 28) they experienced a significant reduction vermicomposting (Figure 2), although later on (days 21 and 28) they experienced a significant in differential abundance (Figure3). This was followed by a significant increase in their abundance reduction in differential abundance (Figure 3). This was followed by a significant increase in their between days 28 and 35, reaching similar levels to those in the beginning, and no more noticeable abundance between days 28 and 35, reaching similar levels to those in the beginning, and no more changes were recorded until the end of the trial (Figure3). The three proteobacterial classes ( Gamma-, noticeable changes were recorded until the end of the trial (Figure 3). The three proteobacterial Alpha-, and ) followed distinct trends over the course of the process (Supplementary classes (Gamma-, Alpha-, and Deltaproteobacteria) followed distinct trends over the course of the Figure S3). process (Supplementary Figure S3). In addition to Proteobacteria, ASVs from the phyla , and Actinobacteria, with minor contributions of the phyla , and , made up about another half of the sequences of the fresh distilled grape marc (Figure 2). Earthworms significantly reduced the abundance of Firmicutes within the first 14 days of vermicomposting followed by no more noticeable differences until day 35 (Figures. 2 and 3), after which its abundance was reduced between this time point and day 42 (Figure 3). A similar trend was observed for the classes and throughout the process of vermicomposting (Supplementary Figure S3). In contrast, the class barely changed in terms of abundance over the course of the process (Supplementary Figure S3). The phylum Bacteroidetes and in particular the class Bacteroidia showed similar values in terms of differential abundance until day 21, followed by a pronounced reduction between days 21 and 28 and a subsequent increase between days 28 and 35 (Figure 3 and Supplementary Figure S3).

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1 0 0 FigureFigure 2. Changes2. Changes in composition in composition of the bacterial of the communities bacterial communities (phylum level) (phylum during vermicomposting level) during ofvermicomposting distilled grape marc of distilled derived grape from marc the whitederived winemaking from the white process winemaking of the grape process variety of the Albariño. grape Thevariety dendrogram Albariño. represents The dendrogram the dissimilarity represents of bacterial the dissimilarity communities of at bacterial the amplicon communities sequence variantat the (ASV)amplicon level (unweightedsequence variant UniFrac (ASV) distances, level (unwei Ward method).ghted UniFrac Bars represent distances, the Ward relative method). abundance Bars of mostrepresent abundant the relative bacterial abundance phyla. Low of abundancemost abundant bacterial phyla. (< 1%) Low were abundance grouped bacterial together. phyla (< 1%) were grouped together. In addition to Proteobacteria, ASVs from the phyla Firmicutes, Bacteroidetes and Actinobacteria, with minorFor the contributions phylum Actinobacteria of the phyla Planctomycetes,and those that appeared Verrucomicrobia in lower and abundance Chloroflexi, (Planctomycetes, made up about anotherVerrucomicrobia half of the and sequences Chloroflexi), of the earthworms fresh distilled led grape to an marcincrease (Figure in its2 ).differential Earthworms abundance significantly after reduced14 days the of abundancevermicomposting of Firmicutes (Figure within3). This the increa firstse 14 also days held of vermicomposting true for the respective followed bacterial by no moreclasses noticeable on day 14 di ff(Supplementaryerences until day Figure 35 (Figures S3). Later2 and on,3), Actinobacteria after which its experienced abundance a was reduction reduced in betweentheir abundance this time between point and days day 21 42 and (Figure 28 (Figure3). A similar 3), while trend the wasabundance observed of forthe theother classes three Clostridiabacterial andphylaNegativicutes remained throughoutwithout noticeable the process changes of vermicomposting from day 14 onwards (Supplementary (Figure 3 Figure and Supplementary S3). In contrast, theFigure class S3).Bacilli barely changed in terms of abundance over the course of the process (Supplementary Figure S3). The phylum Bacteroidetes and in particular the class Bacteroidia showed similar values in terms of differential abundance until day 21, followed by a pronounced reduction between days 21 and 28 and a subsequent increase between days 28 and 35 (Figure3 and Supplementary Figure S3). For the phylum Actinobacteria and those that appeared in lower abundance (Planctomycetes, Verrucomicrobia and Chloroflexi), earthworms led to an increase in its differential abundance after 14 days of vermicomposting (Figure3). This increase also held true for the respective bacterial classes on day 14 (Supplementary Figure S3). Later on, Actinobacteria experienced a reduction in their abundance between days 21 and 28 (Figure3), while the abundance of the other three bacterial phyla remained without noticeable changes from day 14 onwards (Figure3 and Supplementary Figure S3).

Microorganisms 2020, 8, 642 7 of 19 Microorganisms 2020, 8, x FOR PEER REVIEW 7 of 19

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Figure 3. Boxplots showing the changes in the normalized abundance of the most abundant bacterial Figure 3. Boxplots showing the changes in the normalized abundance of the most abundant bacterial phyla during vermicomposting of distilled grape marc derived from the white winemaking process of phyla during vermicomposting of distilled grape marc derived from the white winemaking process the grape variety Albariño. Abundance changes are expressed as log2-fold changes. of the grape variety Albariño. Abundance changes are expressed as log2-fold changes. 3.3. Changes in α- and β-Diversity during Vermicomposting of Distilled Grape Marc 3.3. Changes in α- and β-Diversity during Vermicomposting of Distilled Grape Marc Bacterial alpha-diversity assessed as both ASV richness (Figure4A) and Chao1 richness (SupplementaryBacterial alpha-diversity Figure S4A) was assessed about two as timesboth higherASV richness after 14 days(Figure of vermicomposting 4A) and Chao1 than richness in the (Supplementaryfresh distilled grape Figure marc S4A) (day was 0, Table about1). two A significant times higher increase after on14 daydays 14 of was vermicomposting also observed for than both in theShannon fresh distilled diversity grape (Figure marc S4B (day and 0, Table Table1) 1). and A Faith significant phylogenetic increase diversity on day 14 (Figure was also4B andobserved Table1 for). bothHowever, Shannon while diversity lower values (Figure in ASV S4B andand Chao1Table richness1) and Faith were phylogenetic recorded on day diversity 21 compared (Figure to 4B day and 14 Table(Figure 1).4A, However, Supplementary while Figurelower S4A; values Table in1 ),ASV this reductionand Chao1 was richness not observed were inrecorded Faith phylogenetic on day 21 compareddiversity (Figure to day4 B)14 and (Figure Shannon 4A, diversitySupplementary (Supplementary Figure S4A; Figure Table S4B). 1), Afterwards,this reduction there was was not a observedsignificant in increase Faith phylogenetic in bacterial αdiversity-diversity, (Figure from a4B) taxonomic and Shannon and phylogeneticdiversity (Supplementary viewpoint, between Figure S4B).days 21Afterwards, and 28 (Figure there4A,B was and a significant Supplementary increase Figure in S4A,B),bacterial and α-diversity, no more noticeable from a taxonomic changes were and phylogeneticreported for theviewpoint, duration between of the trial days from 21 and a taxonomic 28 (Figures. perspective 4A,B and (FigureSupplementary4A and SupplementaryFigures S4A,B), andFigure no S4A,B). more noticeable On the contrary, changes the were phylogenetic reported diversity for the ofduration bacterial of communities the trial from was a significantly taxonomic perspectivereduced on the(Figure later time4A and points Supplementary (days 35 and 42), Figure reachings S4A,B). similar On levels the thancontrary, those the reported phylogenetic for days diversity14 and 21 of (Figure bacterial4B). communities was significantly reduced on the later time points (days 35 and 42), reaching similar levels than those reported for days 14 and 21 (Figure 4B).

Microorganisms 2020, 8, 642 8 of 19 Microorganisms 2020, 8, x FOR PEER REVIEW 8 of 19

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FigureFigure 4. 4.Changes Changes in bacterialin bacterialα-diversity α-diversity during during vermicomposting vermicomposting of distilled of distilled grape marcgrape derived marc derived from thefrom white the winemaking white winemaking process ofprocess the grape of the variety grape Albariño: variety Albariño: (A) observed (A) observed amplicon amplicon sequence sequence variant (ASV)variant richness (ASV) and richness (B) faith and phylogenetic (B) faith phylogenetic diversity. Di diversity.fferent letters Different indicate letters significant indicate di ffsignificanterences betweendifferences the di betweenfferent stages the ofdifferent the vermicomposting stages of the process vermicomposting (Tukey Honestly process Significance (Tukey Di ffHonestlyerence (HSDSignificance ) test, false Difference discovery (HSD rate ) (FDR) test, fa corrected).lse discovery rate (FDR) corrected).

Table 1. Results from mixed-effects models are shown for α- and β-diversity indices for vermicomposting of distilled grape marc. Significance was determined using analysis of variance (ANOVA). For each test, we report the relevant F statistic (F5,24) and significance (p(> F)). Degrees of freedom were constant across all tests (numerator degrees of freedom: 5; denominator degrees of freedom: 24).

Alpha Diversity F5,24 p( > F)

Microorganisms 2020, 8, 642 9 of 19

Table1. Results from mixed-effects models are shown for α- and β-diversity indices for vermicomposting of distilled grape marc. Significance was determined using analysis of variance (ANOVA). For each test, we report the relevant F statistic (F5,24) and significance (p(> F)). Degrees of freedom were constant across all tests (numerator degrees of freedom: 5; denominator degrees of freedom: 24).

Alpha Diversity F5,24 p( > F) Observed 12.004 <0.0001 Chao1 9.401 <0.0001 Shannon 54.031 <0.0001 Faith PD 26.615 <0.0001

Beta Diversity F5,24 p-value PCoA1 596.074 <0.0001 Unifrac—unweighted PCoA2 26.350 <0.0001 PCoA1 456.28 <0.0001 Unifrac—weighted PCoA2 6.101 <0.0001 PCoA1 3629.08 <0.0001 Bray–Curtis PCoA2 58.103 <0.0001 PCoA1 2333.82 <0.0001 Jaccard PCoA2 70.029 <0.0001

Principal coordinate analysis using unweighted UniFrac distances showed a clear separation between day 0 (fresh distilled grape marc) and days 14–42 (vermicompost samples) along the first dimension (PCoA1), which accounted for 51.65% of the total variance (Figure5A). The second dimension (PCoA2), which explained 10.03% of the variance, mainly reflected the changes in bacterial community composition between the different stages of the vermicomposting process (Figure5A). The 14- and 21-day samples (i.e., active phase) clustered together and separately from the middle (28 days) and later time points (35 and 42 days, maturation phase). A similar grouping was observed across the days 14, 21, 28, 35 and 42, when day 0 was excluded from the analysis (Figure5B). These trends along PCoA1 and PCoA2 also held true using Bray–Curtis and Jaccard distance matrices, regardless of whether or not day 0 was included (Supplementary Figure S5A,C; Supplementary Figure S5D,F). However, the UniFrac distances showed no significant differentiation among the vermicompost samples along the second principal component (Supplementary Figure S5B,E).

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−0.1 0.0 0.1 0.2 PCoA 1 (24 .14 %)

Figure 5. Changes in bacterial β-diversity during vermicomposting of distilled grape marc derived from the white winemaking process of the grape variety Albariño: (A) principal coordinate analysis (PCoA) of unweighted UniFrac including days 0, 14, 21, 28, 35 and 42; (B) PCoA of unweighted UniFrac across days 14, 21, 28, 35 and 42. Different capital and lower case letters indicate significant pairwise differences between the different stages of the vermicomposting process in PCoA1 and PCoA2 scores, respectively (Tukey HSD test, FDR corrected).

3.4. Core bacterial Microbiome during Vermicomposting of Distilled Grape Marc A total of eighty ASVs were identified as the bacterial core microbiome during vermicomposting of distilled grape marc derived from the grape variety Albariño. These ASVs were present in all of the samples from days 14, 21, 28, 35 and 42 (Figure6), and represented 1.23% of the total ASVs and 8.20% of all sequences. The phyla Proteobacteria (31 ASVs) and Bacteroidetes (21 ASVs) contributed a higher number of ASVs to the core microbiome (Figure6). The phylum Proteobacteria comprised ASVs from the families Rhodobacteraceae, Rhizobiaceae, Sphingomonadaceae and Burkholderiaceae, and Fig. 5 from the genera Devosia, Acinetobacter, Yersinia, Pseudoxanthomonas, and Pseudomonas, among others (Figure6). The phylum Bacteroidetes was mainly represented by ASVs of the genera Flavobacterium and Shingobacterium (Figure6). Other ASVs present in the core microbiome belonged to the phyla Actinobacteria (15 ASVs), Planctomycetes (six ASVs), Verrucomicrobia (four ASVs), Chloroflexi (two ASVs from the order Thermomicrobiales), and Patescibacteria (one ASV from the family Saccharimonadaceae) (Figure6). Microorganisms 2020, 8, x FOR PEER REVIEW 11 of 19

Proteobacteria comprised ASVs from the families Rhodobacteraceae, Rhizobiaceae, Sphingomonadaceae and Burkholderiaceae, and from the genera Devosia, Acinetobacter, Yersinia, Pseudoxanthomonas, Stenotrophomonas and Pseudomonas, among others (Figure 6). The phylum Bacteroidetes was mainly represented by ASVs of the genera Flavobacterium and Shingobacterium (Figure 6). Other ASVs present in the core microbiome belonged to the phyla Actinobacteria (15 ASVs), Planctomycetes (six Microorganisms 2020, 8, 642ASVs), Verrucomicrobia (four ASVs), Chloroflexi (two ASVs from the order Thermomicrobiales), and 11 of 19 Patescibacteria (one ASV from the family Saccharimonadaceae) (Figure 6).

Figure 6. Relative abundance (%) of ASVs (phylum and genus or most inclusive taxonomy found) from the core microbiome of vermicomposting of distilled grape marc derived from theFigure white winemaking6. Relative abundance process of (%) the of grape ASVs variety(phylum Albariño and genus across or most days inclusive 14, 21, 28, taxonomy 35 and 42. found) The initial substrate was not considered for determination of the corefrom microbiome. the core microbiome of vermicomposting of distilled grape marc derived from the white winemaking process of the grape variety Albariño across days 14, 21, 28, 35 and 42. The initial substrate was not considered for determination of the core microbiome.

3.5. Functional Diversity of Bacterial Communities during Vermicomposting of Distilled Grape Marc Our PICRUSt analysis showed a significant increase in genes classified only as “metabolism” in KEGG functional hierarchies after 14 days of vermicomposting, followed by no more noticeable changes until the end of the trial (Figure 7). The same trend was reported for specific genes related to cellulose and lignin metabolism (F20,5 = 7.95, p = 0.0003; F20,5 = 3.86, p = 0.013 respectively; Figure 7 inset), and those involved in the synthesis of salicylic acid (F20,5 = 7.77, p = 0.0003; Figure 7 inset).

Microorganisms 2020, 8, 642 12 of 19

3.5. Functional Diversity of Bacterial Communities during Vermicomposting of Distilled Grape Marc Our PICRUSt analysis showed a significant increase in genes classified only as “metabolism” in KEGG functional hierarchies after 14 days of vermicomposting, followed by no more noticeable changes until the end of the trial (Figure7). The same trend was reported for specific genes related to cellulose and lignin metabolism (F20,5 = 7.95, p = 0.0003; F20,5 = 3.86, p = 0.013 respectively; Figure7 p inset),Microorganisms and those 2020 involved, 8, x FOR PEER in the REVIEW synthesis of salicylic acid (F20,5 = 7.77, = 0.0003; Figure7 inset).12 of 19

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0 14 21 28 35 42 Time (days) Fig. 7 FigureFigure 7. 7.Changes Changes in gene in gene abundance abundance of Kyoto of EncyclopediaKyoto Encyclopedia of Genes ofand Genes Genomes and (KEGG) Genomes orthologies (KEGG) predictedorthologies by predicted the PICRUSt by the software PICRUSt and software classified and as “metabolism”classified as “metabolism” in KEGG functional in KEGG hierarchies functional duringhierarchies vermicomposting during vermicomposting of distilled grape of distilled marc derived grape marcfrom the derived white from winemaking the white process winemaking of the grapeprocess variety of the Albariño. grape variety Individual Albariño. values Individual (n = 5) arevalues plotted (n = for 5) eachare plotted time point for each and time the curve point was and plottedthe curve using was the plotted “loess” using smoothing the “loess” method smoothing in ggplot2. method The insets in ggplot2. show changesThe insets in geneshow abundance changes in ofgene all PICRUSt-predictedabundance of all PICRUSt enzyme-level-predicted genes enzyme for cellulose-level genes and ligninfor cellulose metabolism, and lignin and synthesismetabolism, of salicylicand synthesis acid. Values of salicylic are presented acid. Values as means are presentedstandard as means error ( n± =standard5). error (n = 5). ± 3.6.3.6. ComparisonComparison betweenbetween RawRaw andand DistilledDistilled GrapeGrape MarcMarc Bacterial Bacterial Community Community Composition Composition and and Diversity Diversity TheThe bacterialbacterial richnessrichness ofof distilleddistilled grapegrape marc,marc, assessedassessed asas ASVASV andand Chao1Chao1 richness,richness, waswas aboutabout threethree times times higher higher than than that in that the raw in thegrape raw marc grape at the beginningmarc at the of their beginning respective of vermicomposting their respective trialsvermicomposting (Table2). The sametrials pattern(Table 2). was The observed same pattern for bacterial was observed diversity for estimated bacterial by diversity the Shannon estimated index, by whichthe Shannon was twofold index, higher which in was the distilledtwofold grapehigher marc in the on distilled day 0 (Table grape2). marc At the on end day of 0 the (Table process, 2). At both the theend distilled of the process, and raw both grape the marcsdistilled reached and raw similar grape levels marcs in reached terms of similar bacterial levels richness in terms and of diversity bacterial fromrichness a taxonomic and diversity viewpoint from a (Table taxonomic2), while viewpoint the Faith (Table phylogenetic 2), while diversitythe Faith wasphylogenetic about two diversity times greaterwas about in the two raw times grape greater marc in (Table the raw2). grape marc (Table 2). WhenWhen wewe comparedcompared withwith thethe rawraw grapegrape marcmarc bacterialbacterial communitycommunity compositioncomposition (Table(Table2 ),2), the the relativerelative abundance abundance of of Proteobacteria Proteobacteria was was similar similar to to that that of distilledof distilled grape grape marc marc at the at beginningthe beginning of the of trialthe (daytrial 0).(day However, 0). However, Firmicutes Firmicutes showed showed a higher a higher relative relative abundance abundance in the raw in thanthe raw in the than distilled in the grapedistilled marc grape (Table marc2), while (Table the 2), opposite while the trend opposite was reported trend forwas the reported phyla Bacteroidetes, for the phyla Actinobacteria Bacteroidetes, Actinobacteria and Verrucomicrobia (Table 2). In addition, the phyla Planctomycetes and Chloroflexi appeared as dominant bacterial phyla (>1%) in the fresh distilled grape marc, but this was not the case for the raw grape marc (Table 2). At the end of the vermicomposting trial (day 91 for raw and day 42 for distilled), similar relative abundances of Proteobacteria, Firmicutes, Bacteroidetes, Actinobacteria and Verrucomicrobia were reported for the two winery byproducts (Table 2).

Table 2. Comparison of mean α-diversity indices and mean relative abundances of the dominant bacterial phyla between raw and distilled grape marcs at the beginning and the end of the respective

Microorganisms 2020, 8, 642 13 of 19 and Verrucomicrobia (Table2). In addition, the phyla Planctomycetes and Chloroflexi appeared as dominant bacterial phyla (>1%) in the fresh distilled grape marc, but this was not the case for the raw grape marc (Table2). At the end of the vermicomposting trial (day 91 for raw and day 42 for distilled), similar relative abundances of Proteobacteria, Firmicutes, Bacteroidetes, Actinobacteria and Verrucomicrobia were reported for the two winery byproducts (Table2).

Table 2. Comparison of mean α-diversity indices and mean relative abundances of the dominant bacterial phyla between raw and distilled grape marcs at the beginning and the end of the respective Microorganismsvermicomposting 2020, 8, x FOR trials. PEER Values REVIEW are given as mean standard error. The raw grape marc data were13 of 19 ± taken from Kolbe et al. [25] vermicomposting trials. Values are given as mean ± standard error. The raw grape marc data were End Process End Process taken from Kolbe et al. [25] Day 0 (91 days) (42 days) End process End process Raw Grape Distilled Grape Raw Grape Distilled Grape Alpha Diversity Day 0 Marc Marc (91 days)Marc (42Marc days) Raw grape Distilled grape Raw grape AlphaObserved diversity 95.47 7.66 326.26 16.16 685.20 38.87Distilled 617.14 grape50.72 marc marc± marc± marc ± ± Chao1 100.67 9.54 353.41 17.35 724.43 46.91 637.15 56.05 ± ± ± ± ShannonObserved 2.4095.47 ±0.04 7.66 326.26 4.14 ± 16.160.07 685.20 5.39 ± 38.870.07 617.14 5.29 ± 50.720.08 ± ± ± ± FaithChao1 PD 10.76100.67 ±1.16 9.54 353.41 11.18 ± 17.350.51 724.43 40.62 ± 46.912.53 637.15 27.19 ± 56.050.52 Shannon 2.40± ± 0.04 4.14 ± 0.07± 5.39 ± 0.07± 5.29 ± ±0.08 Relative Faith PD 10.76 ± 1.16 11.18 ± 0.51 40.62 ± 2.53 27.19 ± 0.52 Abundances—Phylum Relative Proteobacteria 58.89 2.08 60.01 3.67 52.00 0.95 52.37 1.366 abundances—Phylum ± ± ± ± Firmicutes 39.17 2.05 18.87 1.95 0.61 0.05 0.45 0.05 Proteobacteria 58.89± ± 2.08 60.01 ± 3.67± 52.00 ± 0.95± 52.37 ±± 1.366 Bacteroidetes 1.09 0.28 14.90 2.82 30.10 1.58 30.29 1.66 Firmicutes 39.17± ± 2.05 18.87 ± 1.95± 0.61 ± 0.05± 0.45 ± ±0.05 Actinobacteria 0.78 0.31 1.34 0.27 9.73 0.94 8.11 0.55 Bacteroidetes 1.09± ± 0.28 14.90 ± ±2.82 30.10 ± 1.58± 30.29 ± 1.66 Verrucomicrobia 0.01 0.008 0.08 0.03 3.13 0.23 4.55 0.14 ± ± ± ± PlanctomycetesActinobacteria 0.050.78 ±0.02 0.31 1.34 not ± detected 0.27 9.73 2.37 ± 0.940.20 not8.11 detected± 0.55 ± ± VerrucomicrobiaChloroflexi 0.0230.01 ± 0.0080.01 0.08 not ± detected 0.03 3.13 1.01 ± 0.230.13 not4.55 detected± 0.14 Planctomycetes 0.05± ± 0.02 not detected 2.37 ± 0.20± not detected Chloroflexi 0.023 ± 0.01 not detected 1.01± 0.13 not detected Based on Venn diagrams ttwentywenty ASVs (5% of the total ASVs) were shared by both winery byproductbyproductss onon dayday 00 (Figure(Figure8 A,8A, Table Table S1), S1) while, while 137 137 and and 224 224 ASVs ASVs were were exclusively exclusively found found in raw in andraw anddistilled distilled grape grape marc, marc, respectively respectively (Figure (8FigureA). When 8A). we When compared we compared the end products the end of products the respective of the respectivevermicomposting vermicomposting trials, raw trials, and distilled raw and grape distilled marc grape shared marc 9% shared of the ASVs9% of (Figurethe ASVs8B). (Figure They had8B). They59 ASVs had in 59 common ASVs in (Figurecommon8B, ( TableFigure S2), 8B, with Table a totalS2), with of 106 a total and 473of 106 ASVs and being 473 ASVs exclusive being of exclusive raw and ofdistilled raw and grape distilled marc grape derived marc vermicomposts, derived vermicomposts, respectively respectively (Figure8B). (Figure 8B).

A) Fresh grape marc

Raw Shared Distilled 137 20 224

Figure 8. Cont.

B) End product

Raw Shared Distilled 106 59 473

Microorganisms 2020, 8, x FOR PEER REVIEW 13 of 19

vermicomposting trials. Values are given as mean ± standard error. The raw grape marc data were taken from Kolbe et al. [25]

End process End process Day 0 (91 days) (42 days) Raw grape Distilled grape Raw grape Alpha diversity Distilled grape marc marc marc marc Observed 95.47 ± 7.66 326.26 ± 16.16 685.20 ± 38.87 617.14 ± 50.72 Chao1 100.67 ± 9.54 353.41 ± 17.35 724.43 ± 46.91 637.15 ± 56.05 Shannon 2.40 ± 0.04 4.14 ± 0.07 5.39 ± 0.07 5.29 ± 0.08 Faith PD 10.76 ± 1.16 11.18 ± 0.51 40.62 ± 2.53 27.19 ± 0.52 Relative

abundances—Phylum Proteobacteria 58.89 ± 2.08 60.01 ± 3.67 52.00 ± 0.95 52.37 ± 1.366 Firmicutes 39.17 ± 2.05 18.87 ± 1.95 0.61 ± 0.05 0.45 ± 0.05 Bacteroidetes 1.09 ± 0.28 14.90 ± 2.82 30.10 ± 1.58 30.29 ± 1.66 Actinobacteria 0.78 ± 0.31 1.34 ± 0.27 9.73 ± 0.94 8.11 ± 0.55 Verrucomicrobia 0.01 ± 0.008 0.08 ± 0.03 3.13 ± 0.23 4.55 ± 0.14 Planctomycetes 0.05 ± 0.02 not detected 2.37 ± 0.20 not detected Chloroflexi 0.023 ± 0.01 not detected 1.01± 0.13 not detected Based on Venn diagrams twenty ASVs (5% of the total ASVs) were shared by both winery byproducts on day 0 (Figure 8A, Table S1), while 137 and 224 ASVs were exclusively found in raw and distilled grape marc, respectively (Figure 8A). When we compared the end products of the respective vermicomposting trials, raw and distilled grape marc shared 9% of the ASVs (Figure 8B). They had 59 ASVs in common (Figure 8B, Table S2), with a total of 106 and 473 ASVs being exclusive of raw and distilled grape marc derived vermicomposts, respectively (Figure 8B).

A) Fresh grape marc

Raw Shared Distilled 137 20 224

Microorganisms 2020, 8, 642 14 of 19

B) End product

Raw Shared Distilled 106 59 473

Figure 8. Venn diagrams showing the shared and exclusive ASVs between raw and distilled grape marc at the (A) beginning (day 0), and (B) end of the respective vermicomposting trials (days 91 and 42 for raw and distilled grape marc, respectively). The raw grape marc data were taken from Kolbe et al. [25].

4. Discussion Vermicomposting of distilled grape marc of the white grapevine cultivar Albariño was characterized by rapid bacterial community compositional changes. After 14 days of vermicomposting, the most striking shift at the phylum level involved a decrease in the abundance of Firmicutes (Figures2 and3), as previously reported by Kolbe et al. [ 25] after only seven days of vermicomposting of raw grape marc obtained from the same grape variety. However, Firmicutes showed similar values in terms of abundance at the earlier time points before decreasing significantly on day 28 in the case of raw grape marc derived from the red grapevine cultivar Mencía [7]. This phylum is considered a fast-growing copiotroph group, while oligotrophic groups such as Actinobacteria, Planctomycetes, Verrucomicrobia and Chloroflexi reached higher levels on day 14, and the four of them, except for Actinobacteria, remained unchanged for the duration of the trial with distilled grape marc (Figure3). Similarly, a rapid increase in Actinobacteria was found by Kolbe et al. [ 25] on day 7, while Gómez-Brandón et al. [7] observed a significant reduction in its abundance on day 14. Oligotrophic and copiotrophic bacterial groups mainly differed with regard to their growth strategies under nutrient rich conditions and their efficiency in metabolizing carbon substrates, i.e., labile and recalcitrant compounds for copiotrophs and , respectively [44]. Although 14 days is a rather short time, earthworms are known to accelerate the rate of organic matter decomposition (Figure1; Domínguez et al. [45]), and consequently alter microbial community in such short timeframes [46]. These early changes in the composition of bacterial communities also held true at class level for the phyla Firmicutes, Actinobacteria, Planctomycetes, Verrucomicrobia and Chloroflexi (Figure S3). However, for Proteobacteria, the different bacterial classes displayed distinct patterns after 14 days of vermicomposting (Figure S3), probably due to the fact that this phylum is considered the most diverse and include a mix of taxa with different physiological strategies [47]. The phylum Bacteroidetes is associated with copiotrophic environments [48], but unlike Firmicutes its abundance was not reduced after 14 days of vermicomposting (Figure3). A similar trend was reported by Kolbe et al. [25] and Gómez-Brandón et al. [7]. Indeed, Kolbe et al. [25] reported an increase in Bacteroidetes within the first 7 days of vermicomposting before decreasing slightly at the end of the process. This could be due to the fact that Bacteroidetes mostly comprise Gram-negative (G ) bacteria − and previous findings based on phospholipid fatty acid (PLFA) analysis has shown that the passage of organic material through the gut of E. andrei reduced the abundance of Gram-positive (G+) bacteria to a greater extent than that of G bacteria [46,49]. This reasoning was consistent with an increase in the − abundance of the other G bacterial phyla including Planctomycetes, Verrucomicrobia and Chloroflexi − Microorganisms 2020, 8, 642 15 of 19 on day 14 (Figure3). However, in the case of G + bacterial phyla, we observed contrasting trends between the phyla Firmicutes and Actinobacteria after 14 days of vermicomposting (Figure3). While the abundance of Firmicutes was reduced on day 14, Actinobacteria reached higher values at this time point compared to the fresh distilled grape marc (Figure3). This discrepancy could be related to the ability of spore formation in Actinobacteria, which might make them more resistant to earthworm gut passage. Indeed, Aira et al. [23] observed that the passage of organic material through the gut of E. andrei increased the Actinobacteria abundance independently of the initial feedstock. The rapid bacterial compositional changes were accompanied by an increase in richness and both taxonomic and phylogenetic diversity of distilled grape marc within the first 14 days of vermicomposting (Figure4; Figure S4), as earlier shown by Kolbe et al. [ 25]. Gómez-Brandón et al. [7] recorded such an increase in bacterial alpha-diversity later on, on day 28. Similar findings were found for other parent materials in which epigeic earthworms led to an increase of bacterial diversity during the first stages of vermicomposting [26,50–52]. While steady and significant increases in bacterial richness and diversity of raw grape marc were reported for the duration of the vermicomposting trial by Kolbe et al. [25] and Gómez-Brandón et al. [7], we observed a reduction in these measurements in the case of distilled grape marc on day 21 (Figure4A). This decrease was not reflected when phylogenetic information was incorporated (Figure4B). This could be due to the fact that such a reduction in taxonomically diversity at this time point affected phylogenetically related taxa that perform complementary functions. At the end of the respective vermicomposting trials, similar levels of bacterial richness and diversity were reached in both the raw and the distilled grape marc from the white grape variety Albariño (Kolbe et al. [25] and this study; Table2). These values were also close to those reported by G ómez-Brandón et al. [7] at the end of vermicomposting with Mencía raw grape marc. Taken together, this indicates that the bacterial community present in the raw and distilled grape marcs was largely affected and modulated by the earthworms’ activity over the course of the vermicomposting process. As a result, the end products tended to be more similar in terms of bacterial diversity and richness despite of the initial differences in the community composition of the starting materials (Table2). The presence of a core of common bacteria was evidenced in the vermicomposted samples (days 14 to 42) obtained from distilled grape marc (Figure6). The core microbiome can be defined arbitrarily at any threshold for presence and/or abundance [53]; here we chose the most restrictive option, that is, one ASV should be consistently found in all of the samples from 14–42 days to be considered within the core microbiome regardless of its abundance. We found that the eighty core bacterial taxa clearly exceeded in number the core microbiome (3 ASVs) of raw grape marc [25]. Such a difference in richness may be related to the differences in earthworm density between our study and Kolbe’s [25]. A higher earthworm density is also likely to result in a faster and massive transformation of the fresh substrate into earthworm casts. In fact, some of the core bacterial genera present in the vermicomposted distilled grape marc (e.g., , , Rhodobacteraceae, Flavobacteriaceae, Pseudomonas, Chryseobacterium, and Acinetobacter) were also previously found in casts of E. andrei [54]. Furthermore, we found in the core microbiome of distilled grape marc members of the phylum Proteobacteria that may contribute to nitrogen fixation (family Burkholderiaceae and genus Devosia that belongs to the order Rhizobiales) and to disease suppression (Pseudomonas)[55]. Chitinophagaceae and other representatives of the phylum Bacteroidetes, which are known to produce a large number of plant cell degrading enzymes with the ability of degrading macromolecules such as chitin and cellulose [56], were also present. Analysis of functional diversity with PICRUSt revealed that vermicomposting of distilled grape marc resulted in a rapid increase in the metabolic capacity of the bacterial community after 14 days followed by no more significant changes for the duration of the trial (Figure7). Despite this increase, the functional diversity over the course of the process was higher in the microbiome of raw grape marc than in the microbiome of distilled grape marc (Kolbe et al. [25]; Figure7 in present study). At the end of the respective trials, the functional diversity in the raw grape marc-derived vermicompost was circa two times higher than that obtained from distilled grape marc (Kolbe et al. [25]; Figure7 in Microorganisms 2020, 8, 642 16 of 19 present study). The strong pressure exerted by certain abiotic factors such as high temperature and low oxygen levels during the process of distillation could have influenced the metabolic capacity of bacterial communities of the fresh distilled grape marc, thereby leading to the subsequent changes throughout the vermicomposting trial. In addition, processing of distilled grape marc through vermicomposting resulted in increases in the abundance of specific genes involved in the breakdown of cellulose and lignin (Figure7 inset), and in specific metabolic processes potentially beneficial for plant growth and development, such as the synthesis of salicylic acid (Figure7 inset). In particular, salicylic acid has been shown to reduce plant stress by inducing plant resistance mechanisms and increasing the antioxidant activity of plants [57]. However, in contrast to Kolbe et al. [25], vermicomposting of distilled grape marc did not lead to an increase in the genes involved in the biosynthesis of (data not shown).

5. Conclusions Proteobacteria and Bacteroidetes dominated the bacterial microbiome over the course of the process as previously shown for raw grape marc, and they contributed with a higher number of ASVs to the core microbiome of distilled grape marc. The compositional changes were accompanied by a rapid increase in richness and taxonomic diversity of bacterial communities on day 14, with values similar to those reported for raw grape marc at the end of the process. Although there was an increase in the metabolic capacity of the bacterial communities after 14 days, the functional diversity of distilled grape marc was lower when compared to raw grape marc. In conclusion, vermicomposting appears as a promising sustainable option to process the valorized distilled grape marc from Albariño grapes, yielding an end product with richer and higher bacterial diversity, and with functional attributes that may enhance the role of distilled grape marc vermicompost for its further use as plant growth promoter and/or soil organic amendment.

Supplementary Materials: The following are available online at http://www.mdpi.com/2076-2607/8/5/642/s1, Figure S1: Rarefaction curves showing the number of amplicon sequence variants (ASV) found in each sample during vermicomposting of distilled grape marc derived from the white winemaking process of the grape variety Albariño. These curves indicate that the sequencing depth was optimal for all of the samples in the full data set. Figure S2: Rarefaction curves showing the number of amplicon sequence variants (ASV) found in each sample during vermicomposting of distilled grape marc derived from the white winemaking process of the grape variety Albariño. These curves indicate that the sequencing depth was optimal for all of the samples in the filtered data set. Figure S3: Boxplots showing the changes in the normalized abundance of bacterial classes of the most abundant phyla during vermicomposting of distilled grape marc derived from the white winemaking process of the grape variety Albariño. Abundance changes are expressed as log2fold. A specific colour is given to the name of the different bacterial classes according to the phylum they belong to. Figure S4: Additional estimates of bacterial α-diversity including A) Chao1 richness and B) Shannon diversity during vermicomposting of distilled grape marc derived from the white winemaking process of the grape variety Albariño. Different letters indicate significant differences between the different stages of the vermicomposting process (Tukey HSD test, FDR corrected). Figure S5: Additional estimates of bacterial β-diversity during vermicomposting of distilled grape marc derived from the white winemaking process of the grape variety Albariño. Principal coordinate analysis with Bray-Curtis (A), weighted UniFrac (B), and Jaccard (C) including days 0, 14, 21, 28, 35 and 42. Principal coordinate analysis with Bray-Curtis (D), weighted UniFrac (E), and Jaccard (F) across days 14, 21, 28, 35 and 42. Different capital and lower case letters indicate significant differences between the different stages of the vermicomposting process in PCoA 1 and PCoA 2 scores, respectively (Tukey HSD test, FDR corrected). Table S1: Shared ASVs between raw and distilled grape marc at the beginning of the vermicomposting trial; Table S2: Shared ASVs between raw and distilled grape marc at the end of the respective vermicomposting trials, that is after 91 and 42 days respectively. Author Contributions: Conceptualization, J.D.; methodology, M.G.-B., M.A., N.S. and J.D.; software, M.A.; validation, M.G.-B., M.A., M.P.-L. and J.D.; formal analysis, M.G.-B., M.A., and J.D..; investigation, M.G.-B., M.A., N.S. and J.D.; resources, M.P.-L. and J.D.; data curation, M.G.-B., M.A.; writing—original draft preparation, M.G.-B., and M.A.; writing—review and editing, M.G.-B., M.A., N.S., M.P.-L. and J.D.; visualization, M.G.-B., M.A., J.D.; supervision, J.D.; project administration, J.D.; funding acquisition, J.D. and M.P.-L. All authors have read and agreed to the published version of the manuscript. Funding: This study was supported by the Spanish Ministerio de Economía y Competitividad (AGL2017-86813-R) and the Xunta de Galicia (grant numbers ED431F 2018/05 and ED431B 2019/038). MGB acknowledges support by the Programa Ramón y Cajal (RYC-2016-21231; Ministerio de Economía y Competitividad). Microorganisms 2020, 8, 642 17 of 19

Acknowledgments: The authors would like to thank Hugo Martínez, Alberto Da Silva and Natalia Ribao for their help with the vermicomposting process, sample collection and DNA extraction. Conflicts of Interest: The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.

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